Introduction Intensification of crop production practices, has enhanced the pesticide use in the agriculture. Among the xenobiotics the herbicides are the most frequently applied agrochemicals (KECSKES, 1976), for improve the yield-production and quality. Apart from the desired toxic effects of some herbicides on weeds, however, the treatments may also have adverse effects on non-target organisms in the soil, in plants (SZENTPETERY et al. 2005, JOLANKAI et al. 2006) and the rhizosphere, like to other results on the GMO-s (VILLANYI et al. 2006). Either the structure or the function of microbial communities may be influenced by pesticide applications. In case of some herbicides the fast degradation, metabolisation is also known by several soil microbes (KATAI et al. 2002). Mechanisms of such toxic or metabolic effects are highly depending on the types and rates of pesticides, the chemical formulations and also the microbial species, exposed. Herbicides are generally most toxic to phototrophic microorganisms through the disruption of photosynthesis (DELORENZO et al. 2000). Beside the reduced applyed rates, the “new generation” herbicides are offering less harmful effects to the beneficial soil-living organisms, by keeping its weed-control capacity throughout the whole vegetation periods (NAGY, 1989). In the agriculture in comparison with conventional herbicides, the Glean (with a 75 % of chlorsulfuron content) can be still 100 times more efficient against the weeds. Regarding the soil biological consequences, an active role in the detoxification of chlorsulfuron by moulds and Actinomycetes was reported in an earlier study (JOSHI et al., 1985). The biodegradation pathway of chlorsulfuron, operated by Aspergillus niger, a common soil fungus was studied under laboratory conditions by BOSCHIN et al. (2003). The fate of chlorsulfuron herbicid could be potentially managed by some soil-microbes in the soils. Several microbial groups from the soil was studied, therefore in their sensitivity to the various doses of the chlorsulfuron (Glean 75) herbicide. There was a timedependent effect considered, when the 3-weeks and 3-months abundance was also assessed in a soil-incubation model-experiment. A simplified, rapid and economic plating method was developed to estimate the abundance of specific microbes from the herbicide treated soil at different application rates.